NO802309L - PROCEDURE FOR DRY PURIFICATION OF REACTION PRODUCTS FROM A FLAMM BURNER - Google Patents

PROCEDURE FOR DRY PURIFICATION OF REACTION PRODUCTS FROM A FLAMM BURNER

Info

Publication number
NO802309L
NO802309L NO802309A NO802309A NO802309L NO 802309 L NO802309 L NO 802309L NO 802309 A NO802309 A NO 802309A NO 802309 A NO802309 A NO 802309A NO 802309 L NO802309 L NO 802309L
Authority
NO
Norway
Prior art keywords
additives
burner
flame
combustion
procedure
Prior art date
Application number
NO802309A
Other languages
Norwegian (no)
Inventor
Sigfrid Michelfelder
Original Assignee
Steinmueller Gmbh L & C
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Steinmueller Gmbh L & C filed Critical Steinmueller Gmbh L & C
Publication of NO802309L publication Critical patent/NO802309L/en

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Classifications

    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L10/00Use of additives to fuels or fires for particular purposes
    • C10L10/02Use of additives to fuels or fires for particular purposes for reducing smoke development
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J7/00Arrangement of devices for supplying chemicals to fire

Description

Oppfinnelsen vedrører en framgangsmåte til rensing av reaksjonsprodukter som oppstår ved flammeforbrenning av brennstoffer, som inneholder forurensninger som for eksempel svovel-, klor- og fluorforbindelser, ved tilførsel av tilsetningsmidler, som binder forurensningene, i forbrenningsrommet. The invention relates to a method for cleaning reaction products that arise from the flame combustion of fuels, which contain pollutants such as sulphur, chlorine and fluorine compounds, by supplying additives, which bind the pollutants, in the combustion chamber.

Det er tidligere kjent framgangsmåter for gjennomfø-ring av tørr rensing av reaksjonsprodukter fra forbrenning av brennstoffer som er forurenset med eksempelvis svovel, There are previously known procedures for carrying out dry cleaning of reaction products from the combustion of fuels that are contaminated with, for example, sulphur,

klor og fluor. Tilsetningsstoffene, som skal binde forurensningene, blir innført i forbrenningsrommet på forskjellige måter. chlorine and fluorine. The additives, which are supposed to bind the pollutants, are introduced into the combustion chamber in different ways.

Ved en første kjent framgangsmåte går en fram slik at tilsetningsmidlene blir innsprøytet ovenfor flammeområdet i forbrenningsrommet ved hjelp av luftstråler. Ulempen med denne kjente framgangsmåten består i at innføringsmåten for tilsetningsmidlene i forbrenningsrommet ikke sikrer at tilsetningsmidlene binder forurensningene. Grunnen til dette er at luftstrålenes forholdsvis ubetydelige blandingsenergi ikke strekker til for å oppnå en tilfredsstillende blandingsgrad for reaksjonsdeltakerne. Blandingen av reaksjonsdeltakerne skjer dessuten for det meste i temperaturområder som er forenlige med optimale reaksjonsbetingelser. En annen ulempe består i at den oppholdstid som står til rådighet til avslut-ning av reaksjonen er utilstrekkelig, fordi innsprøytingen av tilsetningsmidlene vanligvis skjer i reaksjonstrege om-råder. In a first known method, one proceeds so that the additives are injected above the flame area in the combustion chamber by means of air jets. The disadvantage of this known method is that the method of introducing the additives into the combustion chamber does not ensure that the additives bind the contaminants. The reason for this is that the relatively insignificant mixing energy of the air jets is not sufficient to achieve a satisfactory degree of mixing for the reaction participants. The mixing of the reaction participants also mostly takes place in temperature ranges that are compatible with optimal reaction conditions. Another disadvantage is that the residence time available for completion of the reaction is insufficient, because the injection of the additives usually takes place in slow reaction areas.

Ved en annen kjent framgangsmåte går en fram slik at tilsetningsmidlene blir blandet med brennstoffet rett før sistnevnte innføres i brenne.ren. Denne framgangsmåten ut-merker seg i ugunstig retning ved at tilsetningsmidlene blir utsatt for flammens totale temperaturspektrum, og de må gjen- noraløpe temperaturområder som fører til at de blir uvirksom-me. Dette gjelder særlig ved brennstoffer med høy varmeverdi, hvilket nødvendigvis fører til flammer med høye temperaturer. In another known procedure, one proceeds so that the additives are mixed with the fuel just before the latter is introduced into the incinerator. This method has a disadvantage in that the additives are exposed to the entire temperature spectrum of the flame, and they must again run through temperature ranges which cause them to become inactive. This applies in particular to fuels with a high calorific value, which necessarily leads to flames with high temperatures.

Oppfinnelsen har følgelig tatt sikte på å videreutvik-le en framgangsmåte av det slag, som er angitt innlednings-vis, på en slik måte at det sikres at tilsetningsmidlene, The invention has consequently aimed to further develop a method of the kind, which is indicated in the introduction, in such a way that it is ensured that the additives,

som skal binde forurensningene, ved tilførselen blir ført slik sammen med reaksjonsproduktene fra forbrenningen på ett sted og i én form i forbrenningsrommet at det oppnås de for bindingen nødvendige forutsetninger med hensyn til temperatur og blandingsgrad. which is to bind the pollutants, during supply is brought together with the reaction products from the combustion in one place and in one form in the combustion chamber so that the conditions necessary for the binding are achieved with regard to temperature and degree of mixing.

I samsvar med oppfinnelsen er dette oppnådd ved at tilsetningsmidlene blir tilført brennerflammen ved hjelp av en gassformet og/eller flytende bæremiddelstrøm under dannelse av et slør som omgir brennerflammen. In accordance with the invention, this is achieved by the additives being supplied to the burner flame by means of a gaseous and/or liquid carrier stream while forming a veil which surrounds the burner flame.

Som bæremiddel kan det benyttes forskjellige stoffer. Ifølge et første utførelseseksempel på framgangsmåten ifølge oppfinnelsen kan det som bæremiddel benyttes forbrenningsluft i form av en delluftstrøm. Various substances can be used as a carrier. According to a first embodiment of the method according to the invention, combustion air in the form of a partial air flow can be used as a carrier.

Ifølge oppfinnelsen er det også mulig som bæremiddelAccording to the invention, it is also possible as a carrier

å anvende en blanding av forbrenningsluft og røkgass.to use a mixture of combustion air and flue gas.

En annen mulighet er å benytte ren røkgass som bæremiddel for tilsetningene. Another possibility is to use clean flue gas as a carrier for the additives.

Ifølge framgangsmåten kan det som bæremiddel også anvendes en vanlig suspensjon. According to the procedure, a normal suspension can also be used as carrier.

Som tilsetningsmidler kan det benyttes metalloksyder eller hydroksyder i samsvar med patentkrav 6, eller tilset-ninger som angitt i patentkrav 7. As additives, metal oxides or hydroxides can be used in accordance with patent claim 6, or additives as stated in patent claim 7.

Ved at stedet og. formen for tilførselen av tilsetningsmidlene i området for flammen under anvendelse av en gassformet eller flytende bæremiddelstrøm er klart fastlagt på forhånd, blir det oppnådd reaksjonen mellom tilsetningene og forurensningene, fra brenngassene til enhver tid vil foregå der hvor de optimale reaksjonsbetingelser foreligger. By that the place and. the form of the supply of the additives in the area of the flame using a gaseous or liquid carrier flow is clearly determined in advance, if the reaction between the additives and the pollutants is achieved, from the combustion gases at all times will take place where the optimal reaction conditions exist.

Foruten fastsettelsen av stedet og formen for tilførselen av. tilsetningsmidlene kan valget av bæremiddel påvirke reaksjons-prosessen i retning av ytterligere optimalisering. Dette gjelder for eksempel når brennstoffer med høye flammetempera-. turer kan påvirke tilsetningenes virkning i negativ retning. Dessuten kan blandingsforløpet for reaksjonsdeltakerne bli styrt i retning av en reaksjonsoptimalisering gjennom valget av impulsstrømmen for tilsetnings-bæremidlet. Besides the determination of the place and form of the supply of. additives, the choice of carrier can influence the reaction process in the direction of further optimization. This applies, for example, when fuels with high flame temperatures. trips can affect the effects of the additives in a negative direction. In addition, the mixing process for the reaction participants can be controlled in the direction of reaction optimization through the selection of the impulse current for the additive carrier.

Framgangsmåten ifølge oppfinnelsen beskrives i det følgende under henvisning til tegningen som viser en kull-støvbrenner, som framgangsmåten eksempelvis kan anvendes i forbindelse med. The method according to the invention is described in the following with reference to the drawing showing a coal dust burner, with which the method can for example be used.

Med den skjematisk viste brenner, som består av kjer-neluftrør 2, brennstoff- og kullstøv-bæreluftdel 1 og kappe-luftdel 3, blir det frambrakt en primærforbrenningssone 6. Lufttallet for nevnte sone ligger mellom 0,8 oh 1,1 ganger det støkiometriske. With the schematically shown burner, which consists of core air tube 2, fuel and coal dust carrier air part 1 and jacket air part 3, a primary combustion zone 6 is produced. The air number for said zone is between 0.8 and 1.1 times the stoichiometric .

Brenneren er utformet slik at det. ved bestemte for-holdsregler (strømningsbevegelsen for kappeluften, konisk utvidet brennermunning, sluttet kjerneluftstrømning) er frambrakt en sone med intensiv motstrømning 5 i det indre av flammen og fra et område med allerede tiltagende forbrenning. Dette resulterer i hurtig oppvarming og tenning av brennstoff -luftblandingen. Opphetningen og antennelsen av blandingen kan påvirkes ved innstilling av kjerneluftmengden. The burner is designed so that by certain precautions (the flow movement of the jacket air, conically widened burner mouth, closed core air flow) a zone of intensive counterflow 5 is produced in the interior of the flame and from an area of already increasing combustion. This results in rapid heating and ignition of the fuel-air mixture. The heating and ignition of the mixture can be affected by setting the core air quantity.

Den resterende forbrenningsluft blir i form av en delluftstrøm 4, sammen med tilsetningsmidler, som skal binde de gassformete stoffer som dannes, ved forbrenningen, blåst inn via dysen ved omkretsen på en slik måte at det oppstår et delluftstrøm-tilsetningsmiddel-slør omkring flammen. På grunn av nevnte slør utvikler det seg utenfor primærflammen en sekundærflamme eller etterreaksjonssone 7 som via del-luftstrømmen forsynes med oksygen og skadestoffbindende til-setninger. Delluftstrømmen 4 blir derfor anordnet i en del-sirkel som tilsvarer minst den dobbelte kappeluftrørdiamet-eren. Dette sikrer at delluftstrømmen 4 med tilsetningsmidlene først etter en strekning på ca. 1 til 2 ganger kappe-luftrørdiameteren når den egentlige flamme nedstrøms av bren-nermunningen og utenfor de temperaturområder som har svek-kende innvirkning på tilsetningsmidlenes aktivitet. Tilfør-selen av tilsetningsmidlene til delluftstrømmen 4 skjer over en ledning 8, nemlig i området for reguleringsorganet for delluftmengden, ettersom det på dette sted er sikret en god sammenblanding på grunn av strømhvirvlene. The remaining combustion air is blown in via the nozzle at the perimeter in the form of a partial air flow 4, together with additives, which are to bind the gaseous substances that are formed during the combustion, in such a way that a partial air flow-additive veil occurs around the flame. Due to the aforementioned veil, a secondary flame or post-reaction zone 7 develops outside the primary flame, which is supplied with oxygen and pollutant-binding additives via the partial air flow. The partial air flow 4 is therefore arranged in a partial circle which corresponds to at least the double casing air pipe diameter. This ensures that the partial air flow 4 with the additives only after a stretch of approx. 1 to 2 times the jacket air tube diameter reaches the actual flame downstream of the burner mouth and outside the temperature ranges that have a weakening effect on the activity of the additives. The supply of the additives to the partial air flow 4 takes place via a line 8, namely in the area of the regulating body for the partial air quantity, as good mixing is ensured at this location due to the current vortices.

På de avsnitt av flammens omkretsflate, som ikke ligger nær delluftstrømningen 9, blir det ved impulsutbytting suget inn røkgass fra forbrenningsrommet. Dette fører til en nedsettelse av flammetemperaturen, hvilket bidrar til en gun-stig innvirkning på reaksjonsforløpet mellom tilsetning og gassformete skadestoffer. On those sections of the flame's peripheral surface, which are not close to the partial air flow 9, flue gas is sucked in from the combustion chamber by impulse exchange. This leads to a reduction in the flame temperature, which contributes to a favorable effect on the course of the reaction between the additive and gaseous pollutants.

Patentkrav:Patent claim:

1. Framgangsmåte til rensing av reaksjonsprodukter som oppstår ved flammeforbrenning av brennstoffer, som inneholder forurensninger som for eksempel svovel-, klor- og fluorforbindelser, ved tilførsel av tilsetningsmidler, som binder forurensningene, i forbrenningsrommet,karakterisert vedat tilsetningsmidlene blir tilført brenn-flammen ved hjelp av en gassformet og/eller flytende bæremid-delstrøm under dannelse av et slør som omgir brennerflammen. 2. Framgangsmåte i samsvar med krav 1,karakterisert vedat det som bæremiddel blir benyttet forbrenningsluft i form av en delluftstrøm. 3. Framgangsmåte i samsvar med krav 1,karakterisert vedat det som bæremiddel blir benyttet en blanding av forbrenningsluft og røkgass. 4. Framgangsmåte i samsvar med krav 1,karakterisert vedat bæremidlet består av ren røkgass. 5. Framgangsmåte i samsvar med krav 1,karakterisert vedat bæremidlet består av en vandig suspensjon. 6. Framgangsmåte i samsvar med kravene 1 til 5,karakterisert vedat det som tilsetningsmiddel blir benyttet reaksjonsdyktige metalloksyder og hydroksyder av for eksempel metallene natrium, kalium, aluminium, barium, kadmium, kalsium, kobber,: jern, bly, magnesium, mangan og sink. 7. Framgangsmåte i samsvar med kravene 1 til 5,karakterisert vedat det som tilsetningsmidler benyttes støvformete stoffer som kalsiumkarbonat, magnesium-karbonat og dolomitt. 1. Procedure for purification of reaction products which arises from the flame combustion of fuels, which contain pollutants such as sulphur, chlorine and fluorine compounds, by supplying additives, which bind the pollutants, in the combustion chamber, characterized in that the additives are supplied to the combustion flame by means of a gaseous and/or liquid carrier medium stream while forming a veil that surrounds the combustion flame. 2. Method in accordance with claim 1, characterized in that combustion air is used as a carrier in the form of a partial air flow. 3. Method in accordance with claim 1, characterized in that a mixture of combustion air and flue gas is used as carrier. 4. Method in accordance with claim 1, characterized in that the carrier consists of pure flue gas. 5. Method in accordance with claim 1, characterized in that the carrier consists of an aqueous suspension. 6. Method in accordance with claims 1 to 5, characterized in that reactive metal oxides and hydroxides of, for example, the metals sodium, potassium, aluminium, barium, cadmium, calcium, copper, are used as additives: iron, lead, magnesium, manganese and zinc . 7. Method in accordance with claims 1 to 5, characterized in that dust-shaped substances such as calcium carbonate, magnesium carbonate and dolomite are used as additives.

NO802309A 1979-08-11 1980-08-01 PROCEDURE FOR DRY PURIFICATION OF REACTION PRODUCTS FROM A FLAMM BURNER NO802309L (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
DE2932676A DE2932676C2 (en) 1979-08-11 1979-08-11 Process for binding sulfur, chlorine and fluorine compounds during combustion

Publications (1)

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NO802309L true NO802309L (en) 1981-02-12

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US (1) US4331638A (en)
JP (1) JPS5628623A (en)
AU (1) AU537655B2 (en)
BE (1) BE884709A (en)
BR (1) BR8005009A (en)
CA (1) CA1145118A (en)
DE (1) DE2932676C2 (en)
DK (1) DK148927C (en)
ES (1) ES494080A0 (en)
FI (1) FI802498A (en)
FR (1) FR2463180A1 (en)
GB (1) GB2056656B (en)
IN (1) IN152150B (en)
IT (1) IT1131984B (en)
MY (1) MY8500216A (en)
NL (1) NL8004560A (en)
NO (1) NO802309L (en)
PH (1) PH16504A (en)
SE (1) SE438904B (en)
TR (1) TR21166A (en)
YU (1) YU200880A (en)
ZA (1) ZA804879B (en)

Families Citing this family (45)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE3020145A1 (en) * 1980-05-28 1981-12-10 L. & C. Steinmüller GmbH, 5270 Gummersbach METHOD FOR CLEANING REACTION PRODUCTS
US4447203A (en) * 1980-11-28 1984-05-08 Hampton William J Flame combustion of carbonaceous fuels
DE3106580A1 (en) * 1981-02-21 1982-09-02 L. & C. Steinmüller GmbH, 5270 Gummersbach METHOD FOR MINIMIZING EMISSIONS FROM POLLUTION PLANTS
DE3106526A1 (en) * 1981-02-21 1982-09-16 L. & C. Steinmüller GmbH, 5270 Gummersbach METHOD FOR MINIMIZING EMISSIONS FROM POLLUTION PLANTS
DE3128903C2 (en) * 1981-07-22 1983-09-08 L. & C. Steinmüller GmbH, 5270 Gummersbach "Method for introducing additive into a reaction gas stream"
US4523530A (en) * 1982-02-26 1985-06-18 Sumitomo Metal Industries, Ltd. Powdery coal burner
DE3306795C1 (en) * 1983-02-26 1983-12-15 L. & C. Steinmüller GmbH, 5270 Gummersbach Process for binding sulfur compounds, which are formed as reaction products when burning sulfur-containing fuels in a furnace by adding additives
CH658464A5 (en) * 1983-06-03 1986-11-14 Orfa Ag METHOD FOR THE PRODUCTION OF LOW-POLLUTANT FUEL OR EXHAUST GAS AND DEVICE AND PRESSLING FOR CARRYING OUT THE PROCESS.
DE3325065C2 (en) * 1983-07-12 1986-10-09 L. & C. Steinmüller GmbH, 5270 Gummersbach Process for burning fuel dust
AU577366B2 (en) * 1984-04-27 1988-09-22 Foster Wheeler Energy Corporation Controlled flow, split stream burner assembly with sorbent injection
US4765258A (en) * 1984-05-21 1988-08-23 Coal Tech Corp. Method of optimizing combustion and the capture of pollutants during coal combustion in a cyclone combustor
DE3441726C2 (en) * 1984-11-15 1986-11-20 L. & C. Steinmüller GmbH, 5270 Gummersbach Process for the mixture-intensive injection of additives into the combustion chamber to bind the sulfur during the combustion of fuels containing sulfur and a device for carrying out the process
DE3444469C1 (en) * 1984-12-06 1986-06-19 L. & C. Steinmüller GmbH, 5270 Gummersbach Process and round burner for injecting aqueous additive suspensions in the center of a round burner
FI853615L (en) * 1985-09-20 1987-03-21 Tampella Oy Ab FOERFARANDE FOER MINSKNING AV UTSLAEPPEN AV KVAEVE- OCH SVAVELOXIDER VID FOERBRAENNING AV KVAEVE- OCH SVAVELHALTIGT BRAENSLE.
CA1310807C (en) 1986-05-29 1992-12-01 Roderick Beittel Method for reduction of sulfur products from flue gases by injection of powdered alkali sorbent at intermediate temperatures
SE456642B (en) * 1986-06-03 1988-10-24 Euroc Research Ab SET FOR DIRECT DESULATING OF SMOKE GAS IN AN OLD TOWN
US5246364A (en) * 1986-07-14 1993-09-21 Inland Steel Company Method and apparatus for reducing sulfur dioxide content in flue gases
US5048431A (en) * 1986-07-14 1991-09-17 Inland Steel Company Method and apparatus for reducing sulfur dioxide content in flue gases
DE3704637A1 (en) * 1987-02-14 1988-08-25 Hahn Verfahrenstech Process and apparatus for introducing adsorbent into flue gas ducts
DE3707060A1 (en) * 1987-03-05 1988-09-22 Hoelter Heinz Production of special coals from waste products of coal winning for the reduction of NOx, SO2/SO3, HCl and HF in coal-fired power stations or heating installations which are equipped with a fluidised bed, a moving grate or pulverised coal-firing
US4873930A (en) * 1987-07-30 1989-10-17 Trw Inc. Sulfur removal by sorbent injection in secondary combustion zones
US4960577A (en) * 1988-02-04 1990-10-02 Acurex Corporation Enhanced sorbent injection combined with natural gas reburning for a sox control for coal fired boilers
DE58909147D1 (en) * 1988-03-10 1995-05-04 Siemens Ag METHOD AND DEVICE FOR OPERATING A GAS TURBINE WITH ADDITIONAL SUBSTANCES.
US4940010A (en) * 1988-07-22 1990-07-10 Ogden-Martin Systems, Inc. Acid gas control process and apparatus for waste fired incinerators
US5092254A (en) * 1988-07-22 1992-03-03 Ogden-Martin Systems, Inc. Acid gas control process and apparatus for waste fired incinerators
US4920898A (en) * 1988-09-15 1990-05-01 Trw Inc. Gas turbine slagging combustion system
EP0392054B1 (en) * 1989-04-13 1993-03-17 Siemens Aktiengesellschaft Process and apparatus for reducing the harmful emissions by an incineration plant
US5055031A (en) * 1990-05-07 1991-10-08 John Werner Fire vortex display
US5129818A (en) * 1990-09-14 1992-07-14 Benno Balsiger Method of feeding back exhaust gases in oil and gas burners
CA2057621C (en) * 1991-12-13 1995-11-14 Minoru Fujimori Mobile type medical refuse incinerating vehicle
US5237938A (en) * 1991-12-23 1993-08-24 Rokuro Ito Mobile type medical refuse incinerating vehicle
US5201650A (en) * 1992-04-09 1993-04-13 Shell Oil Company Premixed/high-velocity fuel jet low no burner
SE500419C2 (en) * 1992-10-08 1994-06-20 Flaekt Ab Nozzle for atomizing a liquid with pressurized gas
US6071115A (en) * 1994-03-11 2000-06-06 Gas Research Institute Apparatus for low NOx, rapid mix combustion
US5681159A (en) * 1994-03-11 1997-10-28 Gas Research Institute Process and apparatus for low NOx staged-air combustion
DE19512030C2 (en) * 1995-03-31 1997-04-30 Heidelberger Zement Ag Process for the dry desulfurization of flue gases
DE19607026A1 (en) * 1996-02-24 1997-08-28 Abb Research Ltd Flue gas cleaning process for municipal refuse incineration plants
FI973932A (en) * 1997-10-10 1999-04-11 Kvaerner Pulping Oy Method and Arrangement for Optimizing Oxidation in Combustion of Gaseous and Liquid Fuels
US6206685B1 (en) * 1999-08-31 2001-03-27 Ge Energy And Environmental Research Corporation Method for reducing NOx in combustion flue gas using metal-containing additives
US7803201B2 (en) 2005-02-09 2010-09-28 Headwaters Technology Innovation, Llc Organically complexed nanocatalysts for improving combustion properties of fuels and fuel compositions incorporating such catalysts
US7856992B2 (en) * 2005-02-09 2010-12-28 Headwaters Technology Innovation, Llc Tobacco catalyst and methods for reducing the amount of undesirable small molecules in tobacco smoke
US7357903B2 (en) * 2005-04-12 2008-04-15 Headwaters Heavy Oil, Llc Method for reducing NOx during combustion of coal in a burner
US8079845B2 (en) * 2005-05-10 2011-12-20 Environmental Energy Services, Inc. Processes for operating a utility boiler and methods therefor
US7758660B2 (en) * 2006-02-09 2010-07-20 Headwaters Technology Innovation, Llc Crystalline nanocatalysts for improving combustion properties of fuels and fuel compositions incorporating such catalysts
US20100104555A1 (en) * 2008-10-24 2010-04-29 The Scripps Research Institute HCV neutralizing epitopes

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3748080A (en) * 1971-12-27 1973-07-24 Peabody Engineering Corp Combustion control apparatus using a liquid spray
US3746498A (en) * 1972-01-24 1973-07-17 Combustion Eng Reducing no{11 {11 emissions by additive injection
JPS5543812B2 (en) * 1973-07-25 1980-11-08
US4023921A (en) * 1975-11-24 1977-05-17 Electric Power Research Institute Oil burner for NOx emission control
US4141213A (en) * 1977-06-23 1979-02-27 General Motors Corporation Pilot flame tube
DE2807076C3 (en) * 1978-02-18 1980-06-04 Rheinisch-Westfaelisches Elektrizitaetswerk Ag, 4300 Essen Process for reducing sulfur emissions from boiler furnaces
US4235585A (en) * 1978-03-03 1980-11-25 Anderson Hans Christian Process and composition for neutralization of acidic combustion products and for boiler cleaning

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NL8004560A (en) 1981-02-13
YU200880A (en) 1983-02-28
BR8005009A (en) 1981-02-24
DK148927C (en) 1986-05-12
ES8103821A1 (en) 1981-03-16
FR2463180A1 (en) 1981-02-20
CA1145118A (en) 1983-04-26
DE2932676C2 (en) 1983-01-27
AU6114380A (en) 1981-02-19
JPS5628623A (en) 1981-03-20
TR21166A (en) 1983-11-28
BE884709A (en) 1980-12-01
AU537655B2 (en) 1984-07-05
DK340180A (en) 1981-02-12
IT8023644A0 (en) 1980-07-23
PH16504A (en) 1983-11-08
FI802498A (en) 1981-02-12
IN152150B (en) 1983-10-29
US4331638A (en) 1982-05-25
ES494080A0 (en) 1981-03-16
SE8005571L (en) 1981-02-12
ZA804879B (en) 1981-07-29
GB2056656B (en) 1983-09-01
DE2932676A1 (en) 1981-02-19
SE438904B (en) 1985-05-13
FR2463180B1 (en) 1985-02-22
GB2056656A (en) 1981-03-18
DK148927B (en) 1985-11-18
IT1131984B (en) 1986-06-25
MY8500216A (en) 1985-12-31

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